Anion exclusion effects in compacted bentonites: Towards a better understanding of anion diffusion

Abstract Diffusion of 36Cl− in compacted bentonite was studied using through-diffusion, out-diffusion and profile analysis techniques. Both the bulk dry density of the bentonite and the composition of the external solution were varied. Increasing the bulk dry density of the bentonite resulted in a decrease of both the effective diffusion coefficient and the Cl-accessible porosity. Increasing the ionic strength of the external solutions resulted in an increase of both the effective diffusion coefficient and the Cl-accessible porosity. This can be explained by anion exclusion effects (Donnan exclusion). At high ionic strength values (I ⩾ 1 M NaCl) the Cl-accessible porosity approaches the interparticle porosity. This interparticle porosity is the difference between the total and interlayer porosity of the bentonite. The interlayer porosity was found to depend on the degree of compaction. Up to a bulk dry density of 1300 kg m−3 the interlayer is built up of 3 water layers. Between 1300 and 1800 kg m−3 the interlayer water is reduced from 3 to 2 layers of water. Above 1800 kg m−3 evidence for a further decrease to 1 layer of water was found. These findings are in agreement with X-ray data found in the literature showing a decrease of the basal spacing of montmorillonite (the main clay mineral in bentonite) with increasing degree of compaction. The relationship between the effective diffusion coefficient of Cl− and the diffusion-accessible porosity can be described by an empirical relationship analogous to Archie’s law. To predict the effective diffusion coefficient of Cl− in compacted bentonite, the diffusion coefficient of Cl− in water, the bulk dry density and the ionic strength of the pore water have to be known.

[1]  A. Revil,et al.  Diffusion of ionic species in bentonite. , 2006, Journal of colloid and interface science.

[2]  Ian C. Bourg,et al.  Tracer Diffusion in Compacted, Water-Saturated Bentonite , 2006 .

[3]  N. Lu,et al.  Pore-Scale Analysis of Bulk Volume Change from Crystalline Interlayer Swelling in Na+- and Ca2+-Smectite , 2006 .

[4]  A. Jakob,et al.  Diffusion of 22Na and 85Sr in montmorillonite: evidence of interlayer diffusion being the dominant pathway at high compaction. , 2007, Environmental science & technology.

[5]  S. Savoye,et al.  In-situ diffusion of HTO, 22Na+, Cs+ and I- in Opalinus Clay at the Mont Terri underground rock laboratory , 2004 .

[6]  A. Muurinen,et al.  Diffusion of anions and cations in compacted sodium bentonite , 1994 .

[7]  O. Karnland,et al.  Ion concentration caused by an external solution into the porewater of compacted bentonite , 2004 .

[8]  H. Ohashi,et al.  Diffusion mechanism of chloride ions in sodium montmorillonite. , 2001, Journal of contaminant hydrology.

[9]  A. Muurinen,et al.  Diffusion of Chloride and Uranium in Compacted Sodium Bentonite , 1988 .

[10]  John Crank,et al.  The Mathematics Of Diffusion , 1956 .

[11]  C.A.J. Appelo,et al.  Modelling bentonite–water interactions at high solid/liquid ratios: swelling and diffuse double layer effects , 2004 .

[12]  G. Bolt Soil chemistry. B. Physico-chemical models. , 1979 .

[13]  P. M. Heertjes,et al.  Analysis of diffusion in macroporous media in terms of a porosity, a tortuosity and a constrictivity factor , 1974 .

[14]  R. Pusch,et al.  GMM - a general microstructural model for qualitative and quantitative studies of smectite clays , 1990 .

[15]  Li Yuan-hui,et al.  Diffusion of ions in sea water and in deep-sea sediments , 1974 .

[16]  G. Bolt,et al.  Anion exclusion in soil , 1979 .

[17]  R. Jeffrey,et al.  Pertechnetate Exclusion from Sediments , 1998 .

[18]  H. Ohashi,et al.  Self-Diffusion of Sodium Ions in Compacted Sodium Montmorillonite , 1998 .

[19]  A. Revil,et al.  A triple-layer model of the surface electrochemical properties of clay minerals. , 2004, Journal of colloid and interface science.

[20]  H. Ohashi,et al.  Activation energy for diffusion of chloride ions in compacted sodium montmorillonite , 1998 .

[21]  P. Wersin,et al.  Long-term diffusion experiment at Mont Terri: first results from field and laboratory data , 2004 .

[22]  H. Ohashi,et al.  Effect of Dry Density on Activation Energy for Diffusion of Strontium in Compacted Sodium Montmorillonite , 1996 .

[23]  J. Samper,et al.  DI-B experiment: planning, design and performance of an in situ diffusion experiment in the Opalinus Clay formation , 2004 .

[24]  A. Jakob,et al.  Effect of confining pressure on the diffusion of HTO, 36Cl− and 125I− in a layered argillaceous rock (Opalinus Clay): diffusion perpendicular to the fabric , 2003 .

[25]  J. Samper,et al.  A fully 3-D anisotropic numerical model of the DI-B in situ diffusion experiment in the Opalinus clay formation , 2006 .

[26]  G. E. Archie The electrical resistivity log as an aid in determining some reservoir characteristics , 1942 .

[27]  Sin Autor Overview of laboratory methods employed for obtaining diffusion coefficients in FEBEX compacted bentonite , 2006 .

[28]  L. Charlet,et al.  Fe(II)-Na(I)-Ca(II) Cation Exchange on Montmorillonite in Chloride Medium: Evidence for Preferential Clay Adsorption of Chloride – Metal Ion Pairs in Seawater , 2005 .

[29]  A. M. Garavito,et al.  In situ chemical osmosis experiment in the Boom Clay at the Mol underground research laboratory , 2007 .

[30]  M. Jansson,et al.  Anion diffusion pathways in bentonite clay compacted to different dry densities , 2003 .

[31]  P. Grathwohl,et al.  Tracer diffusion coefficients in sedimentary rocks: correlation to porosity and hydraulic conductivity. , 2001, Journal of contaminant hydrology.

[32]  Peter Pivonka,et al.  Theoretical Analysis of Anion Exclusion and Diffusive Transport Through Platy-Clay Soils , 2004 .

[33]  W. D. Kemper,et al.  Chloride Diffusion in Clay-Water Systems1 , 1966 .